Difference between revisions of "Diuron"

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{{Definition|title=Diruon
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{{Definition|title=diruon
  
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|definition=Diuron is used as a herbicide on a variety of both crop and non-crop areas. It is also used as a mildewcide in paints and stains, and as an algaecide in commercial fish production. <ref name="epa">[http://www.epa.gov/oppsrrd1/REDs/diuron_red.pdf EPA US 2003 Reregistration Eligibility Decision (RED) for Diuron] </ref>}}
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|definition=Diuron is used as a herbicide on a variety of both crop and non-crop areas. It is also used as a mildewcide in paints and stains, and as an algaecide in commercial fish production<ref name="epa">[http://www.epa.gov/oppsrrd1/REDs/diuron_red.pdf EPA US 2003 Reregistration Eligibility Decision (RED) for Diuron] </ref>. }}
  
 
== Notes ==
 
== Notes ==
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{| class="toccolours" border="1" style="float: right; clear: right; margin: 0 0 1em 1em; border-collapse: collapse;"
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! bgcolor="#FF8888" | Dichloromethane
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! bgcolor="#FF8888" | Diuron
 
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| align="center" bgcolor="#FFFFFF" | [[Image:Dichloromethane.PNG|150px|Dichloromethane ]]  
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| align="center" bgcolor="#FFFFFF" | [[Image:Diuron.png|200px|Diuron]]  
 
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! bgcolor="#8888FF" | Formula
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! bgcolor="#8888FF" | Formula  
 
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| align="center" | CH<sub>2</sub>Cl<sub>2</sub>
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| align="center" | C<sub>9</sub>H<sub>10</sub>Cl<sub>12</sub>N<sub>2</sub>O
 
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In the USA diuron has been used since 1967. Durion is mainly used on citrus, berries, asparagus and pineapple. Right-of-way applications (e.g., the area around railroad tracks) are the greatest non-agricultural use of diuron, with approximately 1 million kilograms applied annually.
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In the USA diuron has been used since 1967. Durion is mainly used on citrus, berries, asparagus and pineapple. Right-of-way applications (e.g., on rail road tracks) form the greatest non-agricultural use of diuron, with approximately 1 million kilograms applied annually.
  
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In water durion has a low tendency to adsorb to particles and organic matter, dispite its has a relatively low water solubility of 42 mg/l. It's a stable molecule in terrestrial systems but can be biodegraded by micro-organisms. It is expected to be much less stable in aquatic systems, where it's concentration might be halved in 30 days (according to lab experiments).
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In water durion has a low tendency to [[adsorption|adsorb]] to particles and organic matter, dispite its relatively low water solubility of 42 mg/l. It's a stable molecule in terrestrial systems but can be biodegraded by micro-organisms. It is expected to be much less stable in aquatic systems, with a [[half-life]] of 30 days (according to lab experiments).
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Although it has a low potential towards [[bioaccumulation]], it probably doesn't bioaccumulate or [[biomagnification|biomagnify]] in wild aquatic populations. <ref>[http://www.wsdot.wa.gov/maintenance/pdf/diuron.pdf Washington State Department of Transportation February 2006 Diuron Roadside Vegetation Management Herbicide Fact Sheet]</ref>
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Although it has a low potential towards [[bioaccumulation]], it probably doesn't bioaccumulate or [[biomagnification|biomagnify]] in wild aquatic populations<ref>[http://www.wsdot.wa.gov/maintenance/pdf/diuron.pdf Washington State Department of Transportation February 2006 Diuron Roadside Vegetation Management Herbicide Fact Sheet]</ref>.
  
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It has a low toxicity for mammals, doses above 3,4 g per kg body weight are needed to induce acute toxicity. There is a higher for aquatic organisms: some fish species die at concentrations above 4,3 mg/l and some marine invertebrate species may die at concentrations above 1 mg/l. <ref>[http://extoxnet.orst.edu/pips/diuron.htm www.extoxnet.orst.edu august 17 2009]</ref>. Algae are most vulnerable to the herbicide, it can be toxic for some algae species at concentrations of only 5 µg/l. <ref>[http://www.pesticideinfo.org/List_AquireAcuteSum.jsp?Rec_Id=PC33293&Taxa_Group=Phytoplankton www.pesticideinfo.org august 17 2009]</ref>
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It has a low [[toxic|toxicity]] for [[pollution and marine mammals|mammals]], as doses above 3,4 g per kg body weight are needed to induce acute toxicity. Some [[pollution and pelagic fishes|fish]] and marine invertebrate [[species ]] experience acute toxic effects at diuron concentrations above 4,3 mg/l and 1 mg/l respectively<ref>[http://extoxnet.orst.edu/pips/diuron.htm www.extoxnet.orst.edu august 17 2009]</ref>. Algae are most vulnerable to the herbicide, it can be toxic for some algae species at concentrations of only 5 µg/l<ref>[http://www.pesticideinfo.org/List_AquireAcuteSum.jsp?Rec_Id=PC33293&Taxa_Group=Phytoplankton www.pesticideinfo.org august 17 2009]</ref>.
  
 
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== Environmental standards and legislation ==
 
== Environmental standards and legislation ==
  
 
[[List of priority substances|Included in the water framework list of priority substances]]
 
[[List of priority substances|Included in the water framework list of priority substances]]
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== See also ==
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[http://www.vliz.be/projects/endis/EDnorth.php?showchemprop=true&showeffects=true&chemeffects=true&chemid=251 Diuron on the ED North Database]
 
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==References==
 
==References==
 
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{{author
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|AuthorID=19826
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|AuthorFullName=Daphnis De Pooter
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|AuthorName=Daphnisd}}
  
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[[Category:Coastal and marine pollution]]
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[[Category:Toxicity chemicals]]

Latest revision as of 13:10, 9 August 2020

Definition of diruon:
Diuron is used as a herbicide on a variety of both crop and non-crop areas. It is also used as a mildewcide in paints and stains, and as an algaecide in commercial fish production[1].
This is the common definition for diruon, other definitions can be discussed in the article

Notes

Diuron
Diuron
Formula
C9H10Cl12N2O

In the USA diuron has been used since 1967. Durion is mainly used on citrus, berries, asparagus and pineapple. Right-of-way applications (e.g., on rail road tracks) form the greatest non-agricultural use of diuron, with approximately 1 million kilograms applied annually.

In water durion has a low tendency to adsorb to particles and organic matter, dispite its relatively low water solubility of 42 mg/l. It's a stable molecule in terrestrial systems but can be biodegraded by micro-organisms. It is expected to be much less stable in aquatic systems, with a half-life of 30 days (according to lab experiments). Although it has a low potential towards bioaccumulation, it probably doesn't bioaccumulate or biomagnify in wild aquatic populations[2].

It has a low toxicity for mammals, as doses above 3,4 g per kg body weight are needed to induce acute toxicity. Some fish and marine invertebrate species experience acute toxic effects at diuron concentrations above 4,3 mg/l and 1 mg/l respectively[3]. Algae are most vulnerable to the herbicide, it can be toxic for some algae species at concentrations of only 5 µg/l[4].


Environmental standards and legislation

Included in the water framework list of priority substances


See also

Diuron on the ED North Database


References

  1. ↑ EPA US 2003 Reregistration Eligibility Decision (RED) for Diuron
  2. ↑ Washington State Department of Transportation February 2006 Diuron Roadside Vegetation Management Herbicide Fact Sheet
  3. ↑ www.extoxnet.orst.edu august 17 2009
  4. ↑ www.pesticideinfo.org august 17 2009
The main author of this article is Daphnis De Pooter
Please note that others may also have edited the contents of this article.
Citation: Daphnis De Pooter (2020): Diuron. Available from http://www.coastalwiki.org/wiki/Diuron [accessed on 21-11-2024]
Retrieved from "https://www.coastalwiki.org/w/index.php?title=Diuron&oldid=77588"